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Dr. ir. Ann van Griensven Department of Hydroinformatics and Knowledge Management UNESCO-IHE, the Netherlands Soil and Water Assessment Tool (SWAT)

Soil and Water Assessment Tool (SWAT) - enviroGRIDS. ir. Ann van Griensven. Department of Hydroinformatics and Knowledge Management. UNESCO-IHE, the Netherlands. Soil and Water Assessment

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Dr. ir. Ann van GriensvenDepartment of Hydroinformatics and Knowledge ManagementUNESCO-IHE, the Netherlands

Soil and Water Assessment Tool (SWAT)

Course objectives

Get familiar with SWATWhat are the key processes, key parameters?What are the main application domains?

How can we set up a model (get a bit a feeling)?What are the main data needed?

Outline

IntroductionHydrologyEnvironmental processesSWAT for water policyDataApplications

SWATDeveloped by Jeff Arnold at USDA/ARS Temple, Texas, USAGIS interface (ArcView): DEM, Landuse, Soils maps Open sourcesUser and developers communityswatmodel.tamus.edu

What are the objectives of SWATSimulation of processes at land and water phaseSpatially distributed (different scales)Semi physically based / empirical approachesSimulation of changes (climate, land use, management etc.)Water quantities, incl. different runoff componentsWater quality: Nutrients, Sediments, Pesticides, Bacteria, (algae and oxygen), etc.

…. all that on a daily time step and at different spatial scales and (more or less) readily available data sets!!

wwwhttp://swatmodel.tamus.edu/

Download softwareDownload source code

DocumentationUser group mailing list !

Internet Forum

PublicationsApplications

Philosophy (1)Aims

Management analysisWater, sediments, crops, nutrients,

pesticides

Comprehensive –

Process Interactions

InputReadily available input

Physically based input

Philosophy (2)

• Semi-distributed model Conceptual model

Long term simulationsContinuous Time – Daily/hourly time step

Problem of computational efficiency

Upland Processes

SWAT Watershed System

Channel/Flood PlainProcesses

Interface

GRASS (open sources GIS)Mapwindow (open sources GIS)AVSwat-X (ArcView)ArcSWAT (ArcGIS)

BasinSubbasins (based on DEM)

Weather, Routing

Structure

Channel Processes

BasinSubbasins

Weather, RoutingHydrological Response Units

= Combination of soil type and land use properties

Structure

HRUHydrologicResponseUnit

A unique combination ofland use and soil type

Soil map

Land use map+

HRU (2)

NOT

GEO -

REFERENCED

Totaloutput

+

Output 1 x A x 6

Output 2 x A x 5

Output 3 x A x 8

Output 4 x A x 1

HRU6

581

1

2

3

4

# of pixels

input Output 1

input Output 2

input Output 3

input Output 4

1 unit area

SWAT

SWAT DATABASESHRU parameters

GIS subbasin

Pixels : 20Pixel area = A

GEO -

REFERENCED

ARCVIEW

HRU’s in model

Created on the basis of Land Use maps and Soil Maps + databases (with parameters)!!!

Soil map ↔ lookup table ↔ usersoil.dbf (swat2005.mdb)Land use map ↔ lookup table ↔ crop.dbf (swat2005.mdb)Slope classes (drived from DEM)

Preparing landuse dataLanduse Look up table Database (crop.dbf

Landuse legend (raw)

Reclassified/overlaid Landuse

HydrologyErosionPlant GrowthNutrient CyclingPesticide DynamicsAgricultural Management

HRU Processes

Root Zone

Shallow (unconfined)

Aquifer

Vadose(unsaturated)

Zone

Confining Layer

Deep (confined)

Aquifer

PrecipitationEvaporation and

Transpiration

Infiltration/plant uptake/ Soil moisture redistribution

Surface RunoffLateral Flow

Return FlowRevap from

shallow aquiferPercolation to

shallow aquifer

Recharge to deep aquifer

Flow out of watershed

Hydrologic Balance

How is SWAT solving the problems?

Curve Number Values (many more can be found in the manual)

Soil group Land use

% imper-vious A B C D

Residential 20 51 68 79 84 25 54 70 80 85 30 57 72 81 86 38 61 75 83 87 65 77 85 90 92 Parking, roads, rofs 100 98 98 98 98 Cobbles - 76 85 89 91 Commercia 85 89 92 94 95 Industria 72 81 88 91 93 Open ( park, grass...) > 75% grass cover - 39 61 74 80 50 tot 75% grass cover - 49 69 79 84 Meadow - 30 58 71 78 Woods Open - 45 66 77 73 Dense - 25 55 70 77 Agricultural land - 62 71 78 81

10) - CN

1000( 25.4 = S

1) Wetness condition 2

2) 5 % slopeEmpirical equations exist to adjust for different slopes

Key parameter!

Curve Number Value VariationsSoil Groups

Wetness conditions

ABCD

Deep sand, deep loess (low runoff potential)Sandy loam, shallow loess (low to moderate runoff potential)Clay-loam, shallow sandy loam (moderate to high runoff potential)Heavy plastic clay, swelling soil, silty soil (high runoff potential)

CN1CN2CN3

Dry but above wilting pointAverageAbove field capacity, near saturation

Empirical equations exists to calculate CN1 and CN3 from CN2

Subsurface flow

Upper soil layers

ShallowaquiferDeep

aquifer

lateral flowpercolation

infiltration

return flowloss

Groundwater flow

(Slide from W. Bauwens, 2006)

Erosion

Modified Universal Soil Loss Equation (MUSLE)

V = surface qp = is the peak flow rate K = erodibility factorC = crop management factorPE = the erosion control practice factorLS = slope length and steepness factor.

(LS) (PE) (C) (K) )q (V 11.8 = Y 0.56p

Crop processes

PlantingPlant growth: water, nutrient uptakeHarvesting, Grazing, Kill

2 108400

9

6

3

12

Month

LAI

126

Plant Growth

NO3- NH4

+

Soil Organic Matter

NO2-

manures, wastes and sludge

ammonium fixationclay

mineralization

immobilization

nitrification

immobilization

Symbiotic fixation

NO3-

anaerobicconditions

N2 N2 O

NH3Atmospheric N fixation

leaching

fertilizer fertilizer

Harvest

denitrification

ammonia volatilization

runoff

Nitrogen Cycle

Soil Organic Matter

H2 PO4-

HPO4-2

manures, wastes and sludge

mineralization

immobilization

fertilizer Harvest

manures, wastes, and sludge

Adsorbed and fixedInorganic

Fe, Al, Ca, and clay

runoff

Phosphorous Cycle

Foliar Application

Degradation

Washoff

Infiltration

Leaching

Runoff

Surface Application

Degradation

Pesticide dynamics

Management

Ponds, reservoirsUrban areasAgricultural management

Agricultural management (1)

Crop RotationsRemoval of Biomass as HarvestConversion of Biomass to ResidueTillage / Biomixing of Soil Fertilizer Applications GrazingPesticide ApplicationsFilter strips

Agricultural management (2)

IrrigationSubsurface (Tile) DrainageWater Impoundment (e.g. Rice)

• Urban AreasPervious/Impervious AreasStreet SweepingLawn Chemicals

Urban management

Data for SWAT

Ann van Griensven (UNESCO-IHE)

DataWeather data

RainfallRaingage and RADAR

Temperature

Landuse dataRemote Sensing

Land management

Soils and its attributes

Streamflow (quantity)

Water quality

Presenter�
Presentation Notes�
In order to make the river basin sustainable we monitor the river basin�

Databases in swat2005.mbd• Soil• Land cover / plant growth• Tillage• Fertilizer• Pesticide• Urban• Weather generator

GIS integration

Data preparation (1)

GIS maps:DTMLand useSoil

Databases (in swat2005.mdb)Userwgn.dbfUsersoil.dbfCrop.dbf -> create crop.dat

Data preparation (2)

Lookup tablesFor soilFor land use

Soil map ↔ lookup table ↔ usersoil.dbfLand use map ↔ lookup table ↔ crop.dbf

Preparing landuse data

Landuse Look up table Database (crop.dbf

Landuse legend (raw)

Reclassified/overlaid Landuse

Data preparation (3)

Rainfall dataTable with station names and locations (batch files)Data file for each station

Temperature dataTable with station names and locationsData file for each station

Rainfall data file format

Batch file

Data file

Temperature data file format Data file

Batch file

Data preparation (4)

Climate stationsTable with station names and locations (batch file)Userwgn.dbf with data for each station

Climate stations Batch file

Userwgn.dbf

Userwgn.dbf (long term climatic condition)

Rainfall Statistical parameters derivation

Use pcpSTAT.exeUse ASCII text file format to create Input file (e.g. R002.txt)The line of input data file must be a blankOne column of rainfall data valuesThe record should start Jan 1 and End Dec. 31The missing rainfall values should be assigned -99.0

The outputs (e.g. R002.out)File 1 R002.out: Statistical Analysis of Daily Precipitation data. Directly used in userwgn.dbfFile 2 mean_pcp.st: Average Daily precipitation in MonthFile 3 totalpcp.sta: Total Monthly precipitation

Subbasin:

Input.sub: subbasin (area,…).wgn: weather information (#gage or generate).wus: water use.pnd: pond

Output: output.sub

#

#

##

##

####

###### ##

##

#

#

#

#

3

21

17

20

21

8

7

4

5

10

69

13

1816

12

2219

14

11

15

HRU:

Input.hru: HRU information (area,…).sol: sol data.chm: chemical composition soils.gw: groundwater.mgt: agricultural management (Curve number!)

Output: output.hru

River routing:

Input:.rte: river routing input (morphology, manning, …).swq: stream water quality

Output: output.rte

SWAT i/o files:

../Project/scenarios/default/sim#/txtinout

../Project/scenarios/default/sim#/tablesin

../Project/scenarios/default/sim#/tablesout

Dr. ir. Ann van GriensvenDepartment of Hydroinformatics and Knowledge ManagementUNESCO-IHE, the Netherlands

Dr. Preksedis .M. NdombaDepartment of Water Resources EngineeringUNIVERSITY OF DAR ES SALAAM, TANZANIA

The use of SWAT within the Nile Basin

Rainfall/runoff modelling

Rain gage data versus Satellite data: upper Kagera

Slide by Didier Haguma

Rain gage data versus Satellite data: upper Kagera

Slide by Didier Haguma

Pangani River Basin (Ndomba)

0

50

100

150

200

250

1976

1977

1978

1979

1980

1981

1982

Stre

amflo

w (m

3/s)

obseved simulated

020

4060

80100

120140

160

Aug-76

Jan-78

May-79

Oct-80

Feb-82

Jul-83St

ream

flow

(m3/

s)Observed Simulated

0

50

100

150

200

250

0 100 200Observed streamflow (m3/s)

Est

imat

ed st

ream

flow

(m3/

s)

0

50

100

150

200

250

300

0 20 40 60 80 100

Percent of time discharge is equalled or exceeded

Stre

amflo

w (m

3/s)

Observed Estimated

0

20

40

60

80

100

120

140

02/01/1970

01/07/1970

28/12/1970

26/06/1971

23/12/1971

20/06/1972

17/12/1972

Stre

amflo

w (m

3/s)

Observed Estimated

0

5

10

15

20

25

30

35

40

45

1983

1986

1989

1992

1995

1998

2001

2004

Ave

rage

ann

ual f

low

(m3/

s)

Observed Estimated

Daily

R2=54.6%

Monthly

R2=65%

Annually IVF=100%

Validation, R2=68%

Stochastic rainfall modelling: Kyoga

After Max Kigobe

Rainfall interpollation: Nzoia

Water scarcity

Lake Tana

-3.99- -3

-2.99 - -2

-1.99- -1

-0.99 - -0.50

-0.5 - 0.5

0.5 - 1

1 - 2

2 - 3

SMDI Jan, 2005

Lake T

-3.99-

-2.99 -

Drought indexes: upper Blue Nile

Slide by Rahel Tessema

Water resources managament... Jurgen Schuol & Karim Abbaspour

Blue water

Green water flow

Slide by Jurgen Schuol

Erosion/sediment transport

Erosion transport in Pangani (Ndomba)

After Preksedis Ndomba

Blue Nile: Erosion transport Getnet Dubale, UNESCO-IHE, 2009

SWAT + SOBEK

Upper Kagera river: erosion

Environmental problems

Kirumi wetlandImportant part of ecosystem, supports lives of about 6000 peopleSituated on the lower end of the catchmentIt is important to include the wetland in the EFA process

Kirumi wetland

Environmental Flow: Mara catchmentSlide by Florence Mahay

Scenario analysis

DPSIR

Driving forcePressureStateImpactResponse

Climate change and land use change impacts

After Faith Githui

Climate change and land use change impacts

After Faith Githui

Performances

Thank you!